On the Current Debate About Soil Biodiversity

Total Page:16

File Type:pdf, Size:1020Kb

On the Current Debate About Soil Biodiversity Aus dem Institut für Agrarökologie Traute-Heidi Anderson Hans-Joachim Weigel On the current debate about soil biodiversity Manuskript, zu finden in www.fal.de Published in Landbauforschung Völkenrode 53(2003)4, pp. 223- 233 Braunschweig Bundesforschungsanstalt für Landwirtschaft (FAL) 2003 T.-H. Anderson and H.-J. Weigel / Landbauforschung Völkenrode 4/2003 (53):223-233 223 On the current debate about soil biodiversity Traute-Heidi Anderson1 and Hans-Joachim Weigel1 Abstract Zusammenfassung Extreme exploitation and maltreatment of land in a Zur gegenwärtigen Auseinandersetzung zum Thema number of countries had devastating impacts on terrestri- Bodenbiodiversität al ecosystems (i.e., loss of biodiversity of flora and fauna). Biodiversity became a political topic (UNEP, and Con- Da frühere Fälle extremen Raubbaus an Böden und vention on Biological Diversity (CBD) of the United schlechter Bewirtschaftung verheerende Auswirkungen Nations) decades ago and was recently linked to agricul- auf terrestrische Ökosysteme in einer Anzahl von Ländern tural practices in general (OECD, FAO). A survey of hatten (z. B. Verlust der Biodiversität von Flora und reports on “sustainable land use”, “soil fertility”, and Fauna), entwickelte sich der Begriff Biodiversität zu “soil biodiversity” which are published by such organiza- einem politischen Thema und wurde auch erst vor kurzem tions leave the impression that soil fertility is controlled in einen allgemeinen Zusammenhang mit landwirtschaft- by soil biodiversity. In essence this would mean that a low licher Praxis gebracht (OECD, FAO). Eine Sichtung von soil fertility occurs together with a decrease in soil biodi- Berichten über “nachhaltige Landnutzung”, “Boden- versity. Here is the point where assumptions and scientif- fruchtbarkeit” und “Bodenbiodiversität”, die durch diese ic evidence are far apart with respect to below-ground bio- Organisationen veröffentlicht wurden, vermittelt den Ein- diversity. Because the current discussion propagates soil druck, dass Bodenfruchtbarkeit durch Bodenbiodiversität biodiversity as a soil quality indicator, it seems necessary gesteuert bzw. von ihr abhängig sei. Dem Sinn nach würde to question this approach with respect to microbial biodi- dies bedeuten, dass eine geringe Bodenfruchtbarkeit die versity of soils. Biological soil functions such as the main- Folge verminderter Bodenbiodiversität sei. Diese Sicht- tenance of soil fertility are based on the concerted action weise stellt jedoch eher eine Annahme dar, die gegenwär- of soil organisms such as soil microflora and soil fauna. tig durch wissenschaftliche Belege nicht gestützt werden For both biological entities no specific soil functions can kann. Da in der zur Zeit anhaltenden Diskussion über be assigned to species diversity per se. Since organic mat- “Bodenbiodiversität” der Begriff schon als Bodenqua- ter turnover and nutrient turnover are mainly dependent litäts-Indikator vorgeschlagen wird, erscheint es aus on the activity of the soil microbial biomass (bacteria and mikrobiologischer Sicht angebracht, diesen Ansatz zu fungi), the present paper concentrates on this biological hinterfragen. soil fraction. Biologische Bodenfunktionen, wie der Erhalt der An attempt will be made to give an overview of the sci- Bodenfruchtbarkeit, basieren auf der Wechselwirkung entific background of soil microbial biodiversity. Interde- zwischen Bodenorganismen wie der Bodenmikroflora und pendencies between the abiotic and biotic components der Bodenfauna. Für beide biologischen Einheiten kann will be described, together with the relationship between keine bestimmte Bodenfunktion genannt werden, die in above-ground and below-ground biodiversity. irgendeiner Weise mit Artenvielfalt per se in Zusammen- hang zu bringen wäre. Da der Umsatz organischer Sub- Keywords: soil microbial biodiversity, eco-physiological stanz und der Umsatz von Nährstoffen in der Hauptsache quotients, fungal:bacterial ratio, Cmic/Corg ratio, qCO2 von der Aktivität der mikrobiellen Biomasse des Bodens (Bakterien und Pilze) abhängig ist, konzentrieren sich die Ausführungen auf diese biologische Bodenfraktion. Es wird versucht, Hintergrundwissen zum Thema mikrobielle Biodiversität von Böden aus der einschlägi- gen Literatur zusammenzustellen. Wechselwirkungen zwischen abiotischen und biotischen Komponenten von Böden finden ebenso Berücksichtigung wie die Bezie- hung zwischen der oberirdischen und unterirdischen Bio- diversität. Schlüsselworte: mikrobielle Bodenbiodiversität, ökophy- 1 Institute of Agroecology, Federal Agricultural Research Centre (FAL), siologische Quotienten, Pilz:Bakterien-Verhältnis, Bundesallee 50, 38116 Braunschweig/Germany Cmic/Corg-Verhältnis, qCO2 224 1 Introduction identify isolated organisms. This does not speak for a quick routine lab procedure. Since intensification of agricultural production was The last decade has produced a great number of scien- identified as one of the major factors of soil destruction tific papers, mainly reviews, reflections or assumptions on and loss of biodiversity per se, international organizations soil microbial biodiversity and ecosystem function (i.e. (United Nations Conference on the Human Environment Turco et al., 1994; Beare et al., 1995; Kennedy and Smith, (UNEP), 1972; Convention on Biological Diversity 1995; Bengtsson, 1996, 1998; Wolters, (ed.), 1997; Giller (CBD)1992; OECD, 2001) have provided the necessary et al., 1997; Sparling, 1997; Bowman, 1998; Andrén and platform and have worked out strategies on how to pro- Balandreau, 1999; Wardle et al., 1999a,b). Taken together, ceed in order to introduce and keep “sustainable land use” the majority of information given here does not allow the a political issue. In discussing ways how to protect terres- conclusion to be drawn that soil biodiversity regulates soil trial ecosystems with their natural resources and biota fertility. On the contrary, the majority of authors advocate against irreversible losses, they have called upon their an opinion which was provocatively expressed by Bengts- members to contribute indicators which would be applica- son (1996) “there is no (direct) mechanistic relationship ble to many countries and would be helpful to policy mak- between diversity and ecosystem function. To think that ers for law enforcement. The following are excerpts of a one single number - species richness or a diversity index paper held at the OECD Expert Meeting on Soil Erosion - can capture the complex relationships between many and Soil Biodiversity Indicators, Rome, March 2003. species and the functional roles of these interactions is With respect to indicators for agriculture, “soil (micro- ..naive .. and negates most ecological research since the bial) biodiversity” is generally linked to “soil fertility” 1960s”. (FAO, 2001). Here assumptions and scientific evidence do The objective of this paper is to give a short overview of not agree. It is difficult to trace the first appearance of this the scientific information on soil microbial diversity. The combination of “soil biodiversity - soil fertility”. With intention is to point out the weakness of “soil biodiversi- respect to the impacts of agricultural management on ty” as an indicator of soil functions, particularly whenev- soils, attention has focused since the outset on identifying er a link between soil fertility and microbial biodiversity possible bio-indicators, specifically also microbiological is attempted. Since nutrient turnover for plant growth is a bio-indicators which are suitable for defining “soil quali- key function of the soil microbial decomposer communi- ty” or “soil health” (Lynch and Elliott, 1997; Dighton, ty, the present paper concentrates on this biological frac- 1997; Doran and Safley, 1997; Elliott, 1997). The defini- tion. Alternative microbial indicators for soil monitoring tions given for these two terms are actually interchange- purposes are proposed. able, whereby “soil health” comprises more the biological components of soils, i.e. “ the ability of a soil to perform 2 Species richness of soil microorganisms and ecosys- functions that are required for the biological components tem development of an ecosystem...” (Dick, 1997). Pankhurst (1997) in his review assessed the possible link between soil biodiversi- Not every natural soil ecosystem contains the same ty, soil functional processes and soil health while Altieri number of taxonomic entities. Traditionally ecologists (1999) takes a very isolated position in that he indeed sees determine the degree of species richness or diversity by a relationship between soil biodiversity and soil fertility simply counting all species in an area (or sample) of inter- with respect to crop production management. Since one est. By weighting the relative abundance of one species to functional process of the microbial community is the the total number of species, a qualitative index can be turnover of nutrients and therewith the maintenance of obtained which can differentiate between rare and domi- “soil fertility,” the pressure to aggregate viewpoints may nant species (Krebs, 1985). This information can be of have produced this oversimplification: soil biodiversity ecological significance. Microbial ecologists have adopt- predicts soil fertility. ed this procedure when trying to quantify below-ground Except for extreme soil conditions - such as deserts - biodiversity. It is an accepted ecological concept that the soil harbors the most diverse biotic communities on earth. set of environmental conditions shapes
Recommended publications
  • Non-Timber Forest Products
    Agrodok 39 Non-timber forest products the value of wild plants Tinde van Andel This publication is sponsored by: ICCO, SNV and Tropenbos International © Agromisa Foundation and CTA, Wageningen, 2006. All rights reserved. No part of this book may be reproduced in any form, by print, photocopy, microfilm or any other means, without written permission from the publisher. First edition: 2006 Author: Tinde van Andel Illustrator: Bertha Valois V. Design: Eva Kok Translation: Ninette de Zylva (editing) Printed by: Digigrafi, Wageningen, the Netherlands ISBN Agromisa: 90-8573-027-9 ISBN CTA: 92-9081-327-X Foreword Non-timber forest products (NTFPs) are wild plant and animal pro- ducts harvested from forests, such as wild fruits, vegetables, nuts, edi- ble roots, honey, palm leaves, medicinal plants, poisons and bush meat. Millions of people – especially those living in rural areas in de- veloping countries – collect these products daily, and many regard selling them as a means of earning a living. This Agrodok presents an overview of the major commercial wild plant products from Africa, the Caribbean and the Pacific. It explains their significance in traditional health care, social and ritual values, and forest conservation. It is designed to serve as a useful source of basic information for local forest dependent communities, especially those who harvest, process and market these products. We also hope that this Agrodok will help arouse the awareness of the potential of NTFPs among development organisations, local NGOs, government officials at local and regional level, and extension workers assisting local communities. Case studies from Cameroon, Ethiopia, Central and South Africa, the Pacific, Colombia and Suriname have been used to help illustrate the various important aspects of commercial NTFP harvesting.
    [Show full text]
  • BEYOND the STATUS QUO: 2015 EQB Water Policy Report
    BEYOND THE STATUS QUO: 2015 EQB Water Policy Report LAKE ST. CROIX TABLE OF CONTENTS Introduction . 4 Health Equity and Water. 5 GOAL #1: Manage Water Resources to Meet Increasing Demands . .6 GOAL #2: Manage Our Built Environment to Protect Water . 14 GOAL #3: Increase and Maintain Living Cover Across Watersheds .. 20 GOAL #4: Ensure We Are Resilient to Extreme Rainfall . .28 Legislative Charge The Environmental Quality Board is mandated to produce a five year water Contaminants of Emerging Concern . .34 policy report pursuant to Minnesota Statutes, sections 103A .204 and 103A .43 . Minnesota’s Water Technology Industry . 36 This report was prepared by the Environmental Quality Board with the Board More Information . .43 of Water and Soil Resources, Department of Agriculture, Department of Employment and Economic Development, Department of Health, Department Appendices available online: of Natural Resources, Department of Transportation, Metropolitan Council, • 2015 Groundwater Monitoring Status Report and Pollution Control Agency . • Five-Year Assessment of Water Quality Degradation Trends and Prevention Efforts Edited by Mary Hoff • Minnesota’s Water Industry Economic Profile Graphic Design by Paula Bohte • The Agricultural BMP Handbook for Minnesota The total cost of preparing this report was $76,000 • Water Availability Assessment Report 2 Beyond the Status Quo: 2015 EQB Water Policy Report Minnesota is home to more than 10,000 lakes, 100,000 miles of rivers and streams, and abundant groundwater resources. However, many of these waters are not clean enough. In 2015, we took a major step toward improving our water by enacting a law that protects water quality by requiring buffers on more than 100,000 acres of land adjacent to water.
    [Show full text]
  • Gender and Non-Timber Forest Products
    Gender and non-timber forest products Promoting food security and economic empowerment Marilyn Carr, international consultant on gender, technology, rural enterprise and poverty reduction, prepared this paper in collaboration with Maria Hartl, technical adviser for gender and social equity in the IFAD Technical Advisory Division. Other staff members of the IFAD Technical Advisory Division contributing to the paper included: Annina Lubbock, senior technical adviser for gender and poverty targeting, Sheila Mwanundu, senior technical adviser for environment and natural resource management, and Ilaria Firmian, associate technical adviser for environment and natural resource management. The following people reviewed the content: Rama Rao and Bhargavi Motukuri (International Network for Bamboo and Rattan), Kate Schreckenberg (Overseas Development Institute), Nazneen Kanji (Aga Khan Development Network), Sophie Grouwels (Food and Agriculture Organization of the United Nations) and Stephen Biggs (School of Development Studies, University of East Anglia). The opinions expressed in this book are those of the authors and do not necessarily represent those of the International Fund for Agricultural Development (IFAD). The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of IFAD concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The designations ‘developed’ and ‘developing’ countries are intended for statistical convenience and do not necessarily express a judgement about the stage reached by a particular country or area in the development process. Cover: Women make panels and carpets from braided coconut leaves at this production unit near Naickenkottai, India.
    [Show full text]
  • Irrigation Management Effects on Soil Fertility and Environmental Impacts
    Irrigation Management Effects on Soil Fertility and Environmental Impacts Mike Cahn, Irrigation and Water Resources Advisor, UCCE Monterey Water Management Needs to be Factored into Soil Fertility Management Costly to build up soil fertility in organic systems Poor water management can lead to loss of nutrients (mostly N and P) Potential water quality impairments from sediment and nutrients in run-off and leachate from organic fields Organic Liquid Fertilizers* (0.1 – 7% N) Activate, Micronized Fertall Liquid Iron Aqua Power Liquid Fish Fertall Liquid MB Azomite Fertall Liquid Zinc Biolink Organic 0/5/5 HFPC Hydrolyzed Fish Powder Biolink Organic 5/5/5 Maxicrop Kelp Extract Biolink•5-1-1 Organic liquidMicronutrients costs $9.6Micro Hume per lb of N Cranford's Micronized Compost Micro Phos Diamond•13-0-0 K Solution dry grade Gypsumcosts $4 Multi-Ke-Min per lb of N Earth Juice Bloom 0/3/1 Neptune's Harvest Liquid Fish Earth Juice Catalyst Nutra Min Earth Juice Grow 2/1/1 Omega 1/5/5 Eco-Hydro•A substantial fish Liquid amountOmega 6/6/6of the N Eco-Nereo Kelp and Humic Acids Phytamin 800 Eco-Polycould 21 mciro be Shrimp in mineralSolubor form Boron (12-50%) Feather Tea Sulfate of Potash, Diamond K Soluble Fertall Liquid Chelate Calcium *Organic Material Research Institute, National Organic Program Compost sources of Nitrogen • $1.5 - $2 per lb of N (1.4% N product) Cover Crops as a Source of Nitrogen •100 – 150 lb of N/acre in above ground Biomass •Production costs of $150 – $200/acre for a winter cover crop •$1-2 per lb of Nitrogen •Roughly
    [Show full text]
  • The Soil Fertility and Drainage Indexes: 2 United States Forest Service, Fort Collins, CO Taxonomically Based, Ordinal Estimates of Relative Soil Properties Bradley A
    1 Michigan State University, East Lansing, MI The Soil Fertility and Drainage Indexes: 2 United States Forest Service, Fort Collins, CO taxonomically based, ordinal estimates of relative soil properties Bradley A. Miller1, Randall J. Schaetzl1, Frank Krist Jr.2 Validation of the Soil Fertility Index Among other validation approaches with different data sets, 2009 crop yield data for 11 Midwestern states were used to evaluate the FI. In a GIS, we determined the soils and crops in particular fields, and thus were able to ascertain the mean FI value per soil, per crop, per county. These crop specific, mean, county level FI values were then compared with the county yield values reported by USDA-NASS. Statewide summaries of these data produced correlations among yields of specific crops and FI values that were all positive. Below are selected examples. Illinois Crop Rs value Corn 0.73 Soybeans 0.75 Winter Wheat 0.78 Minnesota Crop Rs value Corn 0.29 Soybeans 0.23 Oats 0.80 Sugar Beets 0.24 Low Soil Fertility Index Soil Drainage Index This poster introduces a new, ordinally based, Soil Fertility Index (FI). The above map shows the FI for the lower 48 states. The FI uses family-level The map above shows the natural, inherent, soil wetness of the lower 48 states, as determined by the ordinally based Soil Taxonomy information, i.e., interpretations of taxonomic features or properties that tend to be associated with natural low or high soil Natural Soil Drainage Index (DI). The DI is intended to reflect the amount of water that a soil can supply to growing plants under Wisconsin fertility, to rank soils from 0 (least fertile) to 19 (most fertile).
    [Show full text]
  • Soil Ph and Soil Fertility
    Soil pH and Soil Fertility Dave Wilson Research Agronomist March 7, 2013 Environmental factors influencing plant growth – Which can we manage? 1. Temperature 2. Moisture Supply 3. Radiant Energy (Sunlight: quality, intensity & duration) 4. Composition of the atmosphere 5. Gas content of the soil 6. Soil reaction (Soil pH) Degree of acidity or alkalinity 7. Biotic factors (Plant variety type- genetics, soil biology) 8. Supply of mineral nutrient elements What is pH? • pH can be viewed as an abbreviation for Power of concentration of Hydrogen ion in solution • pH = - [log (H+)] in solution, The pH of a soil is a measure of hydrogen ion activity or concentration ([H+]) in the soil solution. Impact of soil PH changes As the H+ activity increases, soil pH decreases. As the soil pH decreases, most desirable crop nutrients become less available while others, often undesirable, become more available and can reach toxic levels. Total pH scale: 0 ------------------------------ 7 -------------------------------- 14 Acid Neutral Basic or Alkaline The relative availability of Nutrients as a function of pH Color coded chart of relative nutrient availability with change in pH. The darker the blue the more available the nutrient Logarithmic Scale of pH Total pH scale: 10x 0 ---1----2----3----4-----5-----6----- 7 -----8-----9----10-----11-----12-----13--- 14 100x Acid Neutral Basic or Alkaline • Hydrogen activity is mathematically expressed as a negative logarithm: • pH = -log[H+]. Because of the logarithmic scale, one unit decrease in pH implies a 10
    [Show full text]
  • Appendices Soil Quality/Soil Health Cards
    Appendices Appendices v Soil Quality/Soil Health Cards 1. Willamette Valley Soil Quality Card 2. Maryland Soil Quality Assessment Book v Readings (not included in Web version) 1. Farmer/Scientist Focus Sessions: A How-to Guide (1993). D. McGrath, L.S. Lev, H. Murray, R.D. William. Oregon State University Extension Service, EM 8554. 2. How Farmers Assess Soil Health and Quality (1995). D.E. Romig, M.J. Garlynd, R.F. Harris, K. McSweeney. Journal of Soil and Water Conservation. 50(3): 229- 236. 3. The Changing Concept of Soil Quality (1995). B.P. Warkentin. Journal of Soil and Water Conservation. 50(3): 226-228 Permission for reprints in this guide was obtained from authors and publishers. v NRCS State Technical Notes 1. Maryland Soil Quality Assessment Book Technical Note 2. NRCS State Technical Note: Oregon Soil Quality Cards v Soil Quality Card User Guide (not included in Web version) Sample of the Willamette Valley Soil Quality Card Guide (1998). J. Burket et al. Oregon State University Extension Service, EM 8710. (Contact OSUES at: http://osu.orst.edu/extension/, or by faxing 541-737-0817.) v Take-home Training Materials Materials provided to (and added to the Guide by) participants in training sessions. 104 Soil Quality Card Design Guide Willamette Valley Soil Quality Assessment Card The Willamette Valley Soil Quality Assessment Card is a standard paper size (8.5” x 11”) pad, which includes user instructions, an assessment calendar, and multiple soil assessment cards (printed on Rite- in-the-Rain paper). The card was also produced as a fold-out brochure for convenient display and distribution.
    [Show full text]
  • Soil-Fertility Standards for Growing Northern Hardwoods in Forest Nurseries '
    SOIL-FERTILITY STANDARDS FOR GROWING NORTHERN HARDWOODS IN FOREST NURSERIES ' By S. A. Wilde, associate professor of soils, and W. E. PATZER, Wisconsin Agricul- tural Experiment Station 2 INTRODUCTION This paper is supplemental to a previous report dealing with soil- fertility standards for growing northern conifers in forest nurseries (9).^ The general principles and technique therein outlined were followed in the present study. The fertility standards for growing northern hardwoods in forest nurseries were arrived at by analysis of soils from normally developed productive stands that included the following species: Yellow birch (Betula lutea Michx. f.), hard maple (Acer saccharum Marsh.), basswood (Tilia americana L.), American elm (Ulmus americana L.), and white ash {Fraxinus americana L.). No attempt was made in the present study to estabhsh fertility standards for the heavy-seeded species, such as oak, hickory, and walnut. During their first growing season such trees feed to a large extent on nutrients of the seed, and are less dependent upon the soil- fertility level. DESCRIPTION OF AREAS SAMPLED As a general rule, northern hardwoods occur in nature as associates of various forest types, namely, hemlock, yellow birch, maple; maple, basswood, elm; oak, maple, ash; oak, ash, hickory, and so forth. De- pending on circumstances, the soil sampling was applied to the entire forest type or to local groups of the species studied. The total number of sampled areas was limited to 200. However, great care was exercised in the selection of localities; stands affected by logging, pasturing, or fire, as well as those young6>r than 100 years, were rejected.
    [Show full text]
  • Soil Fertility Increases with Plant Species Diversity in a Long-Term Biodiversity Experiment
    Oecologia DOI 10.1007/s00442-008-1123-x ECOSYSTEM ECOLOGY - ORIGINAL PAPER Soil fertility increases with plant species diversity in a long-term biodiversity experiment Ray Dybzinski · Joseph E. Fargione · Donald R. Zak · Dario Fornara · David Tilman Received: 18 January 2008 / Accepted: 21 July 2008 © Springer-Verlag 2008 Abstract Most explanations for the positive eVect of than seedlings grown in soil collected beneath monocul- plant species diversity on productivity have focused on the tures. This increase was likely attributable to greater soil N eYciency of resource use, implicitly assuming that resource availability, which had increased in higher diversity com- supply is constant. To test this assumption, we grew seed- munities over the 10-year-duration of the experiment. In a lings of Echinacea purpurea in soil collected beneath distinction akin to the selection/complementarity partition 10-year-old, experimental plant communities containing one, commonly made in studies of diversity and productivity, two, four, eight, or 16 native grassland species. The results we further determined whether the additive eVects of func- of this greenhouse bioassay challenge the assumption of tional groups or the interactive eVects of functional groups constant resource supply; we found that bioassay seedlings explained the increase in fertility with diversity. The grown in soil collected from experimental communities increase in bioassay seedling biomass with diversity was containing 16 plant species produced 70% more biomass largely explained by a concomitant increase in N-Wxer, C4 grass, forb, and C3 grass biomass with diversity, suggesting that the additive eVects of these four functional groups at Communicated by Louis Pitelka. higher diversity contributed to enhance N availability and retention.
    [Show full text]
  • Large-Scale Soil Health Restoration: the Way Forward for Reversing Climate Change While Enhancing Food and Nutrition Security
    Large-Scale Soil Health Restoration: The Way Forward for Reversing Climate Change while Enhancing Food and Nutrition Security This paper describes what is soil health, and lists soil-regenerative agriculture practices that can mitigate and reverse climate change, improve water management, and enhance food and nutrition security. Soil has been overlooked as a natural resource yet it can be an ally in bringing carbon dioxide levels down by being a carbon sink. Healthy soil increases the adaptive capacity of plants to withstand extreme weather conditions, lessening crops failures, making it essential to fight malnutrition, particularly in rural areas. About the Asian Development Bank LARgE-SCALE SOiL ADB’s vision is an Asia and Pacific region free of poverty. Its mission is to help its developing member countries reduce poverty and improve the quality of life of their people. Despite the region’s many successes, it remains home to a large share of the world’s poor. ADB is committed to reducing poverty through inclusive HEALTH RESTORATiON economic growth, environmentally sustainable growth, and regional integration. Based in Manila, ADB is owned by 67 members, including 48 from the region. Its main instruments for the way Forward For reversing helping its developing member countries are policy dialogue, loans, equity investments, guarantees, grants, and technical assistance. Climate Change while enhanCing Food and nutrition seCurity Sununtar Setboonsarng and Elsbeth E. Gregorio NO. 16 adb southeast asia november 2017 working paper series AsiAn Development BAnk 6 ADB Avenue, Mandaluyong City 1550 Metro Manila, Philippines ASIAN DEVELOPMENT BANK www.adb.org ADB Southeast Asia Working Paper Series Large-Scale Soil Health Restoration: The Way Forward for Reversing Climate Change while Enhancing Food and Nutrition Security Sununtar Setboonsarng and Elsbeth E.
    [Show full text]
  • The Basics of Soil Fertility. Shaping Our Relationship to the Soil
    The Basics of Soil Fertility Shaping our relationship to the soil 2004 Ausgabe Deutschland BASIC GUIDE The enhancement of soil ferti li ty was a crucial value already to the pioneers of organic farming, but the conservation of fer- tile soil is not always given enough attention. And yet organic farming depends on good natural soil fer- tility. Exhausted and dam- aged soils cannot offer the desired performance. The cultivation of soil fertility requires a lot of care. This booklet offers a view on soil fertility from diffe rent angles. It deliberately avoids offering universal 'instructions', but rather seeks to provide informa- tion to stimulate new thinking about a sustainable relationship to the soil. 2016 This publication results from the Organic Knowledge Network Arable project net funded by the Horizon 2020 programme of the European Union. arable Why Talk About Soil Fertility? In cultivating the land, we live from and with soil We feel that in many areas, simple fertility. An ecologically vital soil is continuously cause-and-effect observations do not restoring its productivity. If we neglect its needs, match up to our actual living environment. it suffers as a result. The soil loses vitality, and This is why it is more timely and necessary becomes more sensitive to weather and erosion; than ever to see the soil as a complex organ- harvests decline. In organic farming, damage can­ ism instead of a simple chemical-mechanical not be offset by purely technical means. This is why model. an exhausted or degraded soil requires recovery Thomas Fisel, advisor Bioland by means of ecologically sensitive actions, which help the soil to regenerate on its own.
    [Show full text]
  • Soil Fertility in Organic Systems: a Guide for Gardeners and Small Acreage Farmers
    Soil Fertility in Organic Systems: A Guide for Gardeners and Small Acreage Farmers A PACIFIC NORTHWEST EXTENSION PUBLICATION • PNW646 Washington State University • Oregon State University • University of Idaho Soil Fertility in Organic Systems: A Guide for Gardeners and Small Acreage Farmers Table of Contents Introduction ......................................................................................................................................................................................................................................................1 Soil Fundamentals...........................................................................................................................................................................................................................................1 Soil Tilth .....................................................................................................................................................................................................................................................1 Sources of Soil Fertility ........................................................................................................................................................................................................................1 Soil pH ........................................................................................................................................................................................................................................................2
    [Show full text]